EP0253563B1 - Procédé pour éliminer la vapeur de mercure et/ou la vapeur de composés organiques nuisibles et/ou les oxydes d'azote des gaz de rejet d'une installation d'incinération - Google Patents
Procédé pour éliminer la vapeur de mercure et/ou la vapeur de composés organiques nuisibles et/ou les oxydes d'azote des gaz de rejet d'une installation d'incinération Download PDFInfo
- Publication number
- EP0253563B1 EP0253563B1 EP87306035A EP87306035A EP0253563B1 EP 0253563 B1 EP0253563 B1 EP 0253563B1 EP 87306035 A EP87306035 A EP 87306035A EP 87306035 A EP87306035 A EP 87306035A EP 0253563 B1 EP0253563 B1 EP 0253563B1
- Authority
- EP
- European Patent Office
- Prior art keywords
- flue gas
- spray absorption
- process according
- activated carbon
- powdery
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Lifetime
Links
- 239000003546 flue gas Substances 0.000 title claims abstract description 88
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 title claims abstract description 75
- 238000000034 method Methods 0.000 title claims abstract description 68
- 230000008569 process Effects 0.000 title claims abstract description 61
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 title claims abstract description 51
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 title claims abstract description 39
- 230000001473 noxious effect Effects 0.000 title claims abstract description 18
- 150000002894 organic compounds Chemical class 0.000 title claims description 9
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 127
- 238000010521 absorption reaction Methods 0.000 claims abstract description 38
- 239000007921 spray Substances 0.000 claims abstract description 35
- 239000011236 particulate material Substances 0.000 claims abstract description 23
- 239000002250 absorbent Substances 0.000 claims abstract description 21
- 230000002745 absorbent Effects 0.000 claims abstract description 21
- 230000002378 acidificating effect Effects 0.000 claims abstract description 12
- 239000007789 gas Substances 0.000 claims description 35
- 239000002245 particle Substances 0.000 claims description 34
- 229910052799 carbon Inorganic materials 0.000 claims description 32
- 239000010881 fly ash Substances 0.000 claims description 23
- 239000012717 electrostatic precipitator Substances 0.000 claims description 15
- 239000007788 liquid Substances 0.000 claims description 8
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical group [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 claims description 7
- 239000000920 calcium hydroxide Substances 0.000 claims description 7
- 235000011116 calcium hydroxide Nutrition 0.000 claims description 7
- 229910001861 calcium hydroxide Inorganic materials 0.000 claims description 7
- 239000007795 chemical reaction product Substances 0.000 claims description 6
- CDBYLPFSWZWCQE-UHFFFAOYSA-L sodium carbonate Substances [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 claims description 6
- 238000011144 upstream manufacturing Methods 0.000 claims description 6
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 5
- 235000019738 Limestone Nutrition 0.000 claims description 2
- 239000006028 limestone Substances 0.000 claims description 2
- 238000007873 sieving Methods 0.000 claims description 2
- 235000011182 sodium carbonates Nutrition 0.000 claims 1
- 229910052753 mercury Inorganic materials 0.000 abstract description 22
- 238000001179 sorption measurement Methods 0.000 abstract description 14
- 238000000926 separation method Methods 0.000 abstract description 11
- 238000001816 cooling Methods 0.000 abstract description 4
- 239000003344 environmental pollutant Substances 0.000 description 10
- 231100000719 pollutant Toxicity 0.000 description 10
- 239000000463 material Substances 0.000 description 7
- 239000002912 waste gas Substances 0.000 description 7
- 230000000694 effects Effects 0.000 description 6
- 238000000746 purification Methods 0.000 description 6
- 239000003463 adsorbent Substances 0.000 description 5
- 239000010419 fine particle Substances 0.000 description 5
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 4
- 239000003795 chemical substances by application Substances 0.000 description 4
- 239000000460 chlorine Substances 0.000 description 4
- 229910052801 chlorine Inorganic materials 0.000 description 4
- 239000000571 coke Substances 0.000 description 4
- 150000001875 compounds Chemical class 0.000 description 4
- 230000006378 damage Effects 0.000 description 4
- VGGGRWRBGXENKI-UHFFFAOYSA-N 1-chlorodibenzo-p-dioxin Chemical compound O1C2=CC=CC=C2OC2=C1C=CC=C2Cl VGGGRWRBGXENKI-UHFFFAOYSA-N 0.000 description 3
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 3
- 230000004913 activation Effects 0.000 description 3
- 239000007900 aqueous suspension Substances 0.000 description 3
- 230000007423 decrease Effects 0.000 description 3
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 description 3
- 229910000041 hydrogen chloride Inorganic materials 0.000 description 3
- 239000005416 organic matter Substances 0.000 description 3
- 239000000843 powder Substances 0.000 description 3
- 230000009467 reduction Effects 0.000 description 3
- UIIMBOGNXHQVGW-UHFFFAOYSA-M sodium bicarbonate Substances [Na+].OC([O-])=O UIIMBOGNXHQVGW-UHFFFAOYSA-M 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- KVGZZAHHUNAVKZ-UHFFFAOYSA-N 1,4-Dioxin Chemical compound O1C=COC=C1 KVGZZAHHUNAVKZ-UHFFFAOYSA-N 0.000 description 2
- 239000007864 aqueous solution Substances 0.000 description 2
- 239000002802 bituminous coal Substances 0.000 description 2
- 230000003197 catalytic effect Effects 0.000 description 2
- 239000003610 charcoal Substances 0.000 description 2
- 238000004140 cleaning Methods 0.000 description 2
- 239000003245 coal Substances 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000004744 fabric Substances 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 239000011368 organic material Substances 0.000 description 2
- 150000003071 polychlorinated biphenyls Chemical class 0.000 description 2
- 125000005575 polycyclic aromatic hydrocarbon group Chemical group 0.000 description 2
- 229910000030 sodium bicarbonate Inorganic materials 0.000 description 2
- 235000017557 sodium bicarbonate Nutrition 0.000 description 2
- 229910000029 sodium carbonate Inorganic materials 0.000 description 2
- 238000001694 spray drying Methods 0.000 description 2
- WRSMJZYBNIAAEE-UHFFFAOYSA-N 1-chlorodibenzofuran Chemical class O1C2=CC=CC=C2C2=C1C=CC=C2Cl WRSMJZYBNIAAEE-UHFFFAOYSA-N 0.000 description 1
- 238000004438 BET method Methods 0.000 description 1
- BVKZGUZCCUSVTD-UHFFFAOYSA-M Bicarbonate Chemical compound OC([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-M 0.000 description 1
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 1
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 239000001110 calcium chloride Substances 0.000 description 1
- 229910001628 calcium chloride Inorganic materials 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- RCTYPNKXASFOBE-UHFFFAOYSA-M chloromercury Chemical compound [Hg]Cl RCTYPNKXASFOBE-UHFFFAOYSA-M 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 239000000356 contaminant Substances 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 230000003111 delayed effect Effects 0.000 description 1
- 230000001419 dependent effect Effects 0.000 description 1
- 150000004826 dibenzofurans Chemical class 0.000 description 1
- 150000002013 dioxins Chemical class 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 238000010410 dusting Methods 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 150000002240 furans Chemical class 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 238000000227 grinding Methods 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 231100000086 high toxicity Toxicity 0.000 description 1
- 238000002347 injection Methods 0.000 description 1
- 239000007924 injection Substances 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 230000035515 penetration Effects 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 230000000135 prohibitive effect Effects 0.000 description 1
- 238000010298 pulverizing process Methods 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 230000000717 retained effect Effects 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 239000000725 suspension Substances 0.000 description 1
- 238000005979 thermal decomposition reaction Methods 0.000 description 1
- 231100000419 toxicity Toxicity 0.000 description 1
- 230000001988 toxicity Effects 0.000 description 1
- 239000012808 vapor phase Substances 0.000 description 1
- 238000005200 wet scrubbing Methods 0.000 description 1
Images
Classifications
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J15/00—Arrangements of devices for treating smoke or fumes
- F23J15/02—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/54—Nitrogen compounds
- B01D53/56—Nitrogen oxides
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/64—Heavy metals or compounds thereof, e.g. mercury
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/68—Halogens or halogen compounds
- B01D53/70—Organic halogen compounds
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/72—Organic compounds not provided for in groups B01D53/48 - B01D53/70, e.g. hydrocarbons
Definitions
- mercury vapor which in this context means vapor of elementary mercury as well as mercury-containing chemical compounds in vapor phase
- concentrations will be in the range of 100-1 000 14N m 3 .
- chlorodibenzo-dioxins and -furans are represented by the formulae resp., wherein n and m each independently is an integer from 0 through 4 provided that n + m is at least 2.
- the concentration of these compounds in incinerator flue gases varies considerably, dependent primarily on the temperature prevailing in the combustion zone of the incinerator and on the composition of the refuse which is incinerated. Typically the concentration is 0.1-1.0 iLg/N m 3 but substantial variations also outside this range are usual.
- Incinerator flue gases also contain considerable amounts of nitrogen oxides which are not always removed efficiently by the conventional flue gas purification steps using basic absorbants.
- a process for removing mercury vapor from a hot hydrogen chloride-containing flue gas is disclosed in EP-A-0 013 567 (Svenska Flaktfabriken).
- the gas which contains hydrogen chloride and minor amounts of mercury vapor is contacted with powdered calcium hydroxide, preferably in a fluidized bed.
- the hydrogen chloride in the gas reacts with the calcium hydroxide to form calcium chloride which apparently is essential to the removal of mercury.
- said process does not always enable reduction of mercury vapor to the required low levels, and it is without any substantial effect as to removal of the noxious organic material.
- US-A-4,273,747 discloses removal of mercury from hot waste gases by atomizing an aqueous liquid into the waste gases in the presence of fly ash suspended in the gas and subsequently separating the fly ash together with a substantial part of the mercury originally present as vapor. It is essential that by said treatment the gas stream is cooled from a temperature of at least 200 °C to a temperature below 160 °C.
- the aqueous liquid may be just water or it may be an aqueous solution or suspension of an alkaline compound, preferably calcium hydroxide.
- active charcoal or coke is used to remove noxious flue gas components including heavy metals.
- active coal or coke is used in a fixed bed which means that it should be in the form of rather coarse non-dusting particles or granulates which are expensive to produce and are less active than a corresponding powdery adsorbent.
- US-A-4,061,476 discloses a gas purification method in which a pulverulent solid sorption agent is injected into a stream of noxious-contaminant-containing gas subjected to intensive turbulence and subsequently separated from the gas.
- a pulverulent solid sorption agent is injected into a stream of noxious-contaminant-containing gas subjected to intensive turbulence and subsequently separated from the gas.
- powdery filtering charcoal is suggested without indication of the contaminations for which this specific sorption agent is intended.
- the absorbents are advantageously of grain sizes of less than 100 ⁇ m, preferably less than 50 pm.
- the sorption agent is activated carbon in the form of fine particles efficient separation of the carbon from the gas stream cause troubles. This applies both when electrostatic precipitators and fabric filters are used for the separation.
- the present process uses the activated carbon as a fine powder which is suspended in the gas stream and subsequently removed therefrom together with the particulate material formed by the spray absorption process.
- pulverized activated carbon involves certain advantages over the use of a coarse or granulated carbon due to the relatively higher adsorption capacity of the powdery material and the lower price thereof.
- Fine carbon particles are not easily removed by means of a mechanical filter such as a baghouse, since the fine carbon particles tend to block the filter and thereby create an unacceptably high pressure drop over the filter.
- electrostatic precipitators are less efficient than desired to remove fine particles of activated carbon occurring as sole particulate material in a gas stream. This is due to the fact that the carbon particles have a too low electric resistivity (or a too high conductivity) which means that they loose their electric charge when contacting the ground electrode of the electrostatic precipitator. Thereby the carbon particles are not efficiently retained but tend to become resuspended in the gas stream. This results in an unsatisfactory particle separation from the gas stream unless the consumption of electric energy is increased substantially.
- the presence of the particulate material formed by the spray absorption facilitates the recovery of the powdery activated carbon from the gas stream, not only when a baghouse is used as particle separator but also when particle separation is performed by means of an electrostatic precipitator.
- the particulate material formed in the spray absorption process together with any fly ash present and the flue gas acts as filter aid thereby permitting building up of a powder layer having a substantial thickness on the filter surfaces without undue increase of the resistance to gas passage and consequently without a large pressure drop over the filter.
- the fine particles of activated carbon are embedded in the powder layer thus deposited on the filter surface and dust problems due to penetration of the carbon particles through the filter are avoided and increase of pressure drop over the filter is substantially delayed.
- the particulate material formed in the spray absorption process also has the effect of facilitating the removal of the carbon particles because said particulate material by covering the electrode forms a layer into which the small carbon particles are bound and which layer impedes direct contact between the particles and the electrodes whereby undue discharge of the carbon particles is avoided.
- resuspension of the carbon particles in the stream of gas is less likely to take place and the carbon particles are recovered from the electrostatic precipitator in admixture with said particulate material and any fly ash originally present in the flue gas.
- the term « powdery activated carbon is used in a somewhat broader sense than said term is usually applied in commerce.
- said term is not limited to cover materials which have been subjected to an « activation » treatment, e. g. with vapor.
- the term is intented to cover also powdery carbonacious materials such as coal, coke or the like which have an adsorption activity which is not the result of a special activation but which is inherent in the powdery material already when formed, e. g. by grinding or by thermal decomposition.
- the absorption material used in the present process may be substantially cheaper than commercial activated carbon which has usually been subjected to special activation and purification procedures.
- powdery is used to distinguish the carbonacious material used in this process from the granulated activated carbons conventionally used as fixed bed adsorbents for gas purification.
- the very high adsorption efficiency of the activated carbon in the process according to the invention is a result of the improved adsorption conditions provided by the cooling of the gas stream which takes place in the spray absorption process performed immediately after, during or immediately before the introduction of the powdery activated carbon into the gas stream.
- the powdery activated carbon When the powdery activated carbon is injected into the flue gas stream at a location downstream of the spray absorption chamber it is preferred to use a baghouse as particle separator because an intimate contact between flue gas and carbon is obtained when the flue gas passes through the carbon containing layer of particulate reaction products which builds up on the filter surfaces.
- the present process is also suitable for being performed using a plant in which particles are separated by means of an electrostatic precipitator. Since contact between flue gas and collected particulate material is less intimate in an electrostatic precipitator than in a baghouse filter it is preferred to inject the powdery activated carbon into the gas stream at a location at some distance from the electrostatic precipitator, e. g. in the spray absorption chamber or upstream of said chamber.
- the basic absorbent atomized in an aqueous suspension or solution into the spray absorption chamber is preferably calcium hydroxide (hydrated lime, slaked lime), sodium carbonate or hydrogen carbonate or pulverized limestone.
- fly ash from incinerator plants has a certain ability to remove mercury vapor from flue gas when present in the hot flue gas during the cooling thereof by atomizing aqueous liquids into the hot flue gas.
- any fly ash present in the flue gas to be cleaned and only separate it from the gas together with the particulate material comprising reaction products of the basic absorbent with acidic components of the flue gas, non-reacted basic absorbent and activated carbon.
- the process according to the invention may also be successfully performed on flue gas from which the fly ash has been removed in a preceding particle separation step.
- nitrogen oxides are usually present in incinerator flue gases in amounts several orders of magnitude higher than the amounts of mercury and POM, it is preferred to use relatively large quantities of carbon, e. g. 100-500 mg/N m 3 , when an efficient removal of nitrogen oxides is aimed at.
- a duct 1 which carries a stream of hot incinerator waste gas which besides acidic components such as HCI, S0 2 and nitrogen oxides contains mercury vapor and noxious organic matter, especially chlorodibenzodioxin and -furans.
- the waste gas also contains fly ash.
- duct 1 debouches a pipe 2 connected to a pneumatic system 3 for providing a constant amount of powdery activated carbon to the flue gas.
- the system 3 comprises a hopper 4 for powdery activated carbon and a screw feeder 5 adjusted to deliver a constant rate of carbon or controlled to provide carbon in dependency on the amount and composition of the flue gas stream in duct 1.
- the system 3 is provided with pressurized air through conduit 6.
- the carbon may, of course, be injected by any other means suitable for dispersing into the flue gas.
- the carbon powder is entrained by the waste gas in duct 1 and carried to a spray absorption chamber 7.
- an aqueous absorbent such as a suspension of lime of linestone or a solution of sodium carbonate or sodium hydrogen carbonate, provided through duct 8, is atomized to small droplets.
- the water evaporates from the atomized droplets whereby the temperature of the gas decreases substantially and at the same time acidic substances in the waste gas react with the basic absorbent producting a particulate material primarily comprising salts formed by said reaction, together with non-reacted absorbent.
- the pipe 2 may debouch in the very spray absorption chamber 7 (as indicated by the dotted lines).
- a particulate material comprising said reaction products, non-reacted absorbent, possible fly ash and activated carbon may be recovered from the bottom of the spray absorption chamber through 9 whereas the remaining part of said reaction products and non-reacted absorbent and nearly all the activated carbon and fly ash remain suspended in the gas until the gas reaches an electrostatic precipitator 10, in which substantially all particulate material is separated and removed through 11.
- the gas from which a substantial part of mercury vapor and noxious organic matter, especially chlorodibenzo-dioxin and-furans, originally present therein, have been absorped, may be discharged to the atmosphere via a stack 12.
- the system 3 for providing powdery activated carbon injects the carbon at a location downstream of the spray absorption chamber 7.
- the particle collector is a baghouse 13 from where the powdery carbon mixed with particulate material formed in the spray absorption chamber 7 and mixed with any fly ash originally present in the flue gas in duct 1, is recovered through conduit 14.
- This example was performed in a pilot plant of the type depicted in fig. 2 treating 300 N m 3 /h flue gas.
- the temperature of the flue gas supplied through duct 1 varied from 230 °C to 300 °C.
- An aqueous suspension of slaked line was atomized in the spray absorption chamber 7 to obtain a total removal of 80-95 % of acidic components (HCI and 50 2 ) in the process.
- the baghouse 13 was of the pulse jet type.
- Powdery activated carbon was injected between the spray drying absorption chamber and the pulse jet filter in amounts as indicated in table 1 below.
- the powdery activated carbon was of a quality which has a total surface area (determined by the BET method) of 1 000-1 100.m?/g, a pore volume of 0.8-0.95 cm 3 /g and a mesh size corresponding to a screen analysis (passing 44 ⁇ m apertures) of 65-85 %. Microscopic examination indicates that most particles have a diameter of 1 ⁇ m or less.
- the material is produced by pulverizing bituminous coal and is activated by steam treatment.
- the incinerator gas stream used in all four tests had a fly ash content of approximately 2 g/Nm 3.
- the tests were made on an industrial plant receiving 100,000 Nm 3 /hour incinerator flue gas having an approximate temperature of 240-260 °C and a fly ash content of approximately 2,5 g/Nm 3 .
- This example illustrates that also when particle separation takes place by means of an electrostatic precipitator it is possible to achieve an efficient removal of mercury by the present process.
- Incinerator flue gas was applied through duct 1 in an amount of 300 Nm 3 /h.
- the fly ash content of said flue gas was 2 g/Nm 3 and the temperature varied between 203-300 °C.
- the baghouse 13 was of the pulse jet type.
- the temperature of the flue gas before treatment was 240-280 °C.
- This example demonstrates the ability of the present process for reducing the amount of nitrogen oxides in the flue gas from incinerator plants.
- the incinerator flue gas was supplied in an amount of approximately 60,000-100,000 Nm 3 /h at a temperature of approx. 240-280 °C.
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- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- General Chemical & Material Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Biomedical Technology (AREA)
- Analytical Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Treating Waste Gases (AREA)
- Catalysts (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
Claims (10)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
AT87306035T ATE49714T1 (de) | 1986-07-16 | 1987-07-08 | Verfahren zur entfernung von quecksilberdampf und/oder daempfen schaedlicher organischer verbindungen und/oder stickstoffoxiden aus rauchgas von einer verbrennungsanlage. |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DK3381/86 | 1986-07-16 | ||
DK338186A DK158376C (da) | 1986-07-16 | 1986-07-16 | Fremgangsmaade til nedbringelse af indholdet af kviksoelvdamp og/eller dampe af skadelige organiske forbindelser og/eller nitrogenoxider i roeggas fra forbraendingsanlaeg |
Publications (3)
Publication Number | Publication Date |
---|---|
EP0253563A1 EP0253563A1 (fr) | 1988-01-20 |
EP0253563B1 true EP0253563B1 (fr) | 1990-01-24 |
EP0253563B2 EP0253563B2 (fr) | 1996-04-17 |
Family
ID=8122222
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
EP87306035A Expired - Lifetime EP0253563B2 (fr) | 1986-07-16 | 1987-07-08 | Procédé pour éliminer la vapeur de mercure et/ou la vapeur de composés organiques nuisibles et/ou les oxydes d'azote des gaz de rejet d'une installation d'incinération |
Country Status (9)
Country | Link |
---|---|
US (1) | US4889698B1 (fr) |
EP (1) | EP0253563B2 (fr) |
JP (1) | JPH0829219B2 (fr) |
AT (1) | ATE49714T1 (fr) |
CA (1) | CA1300347C (fr) |
DE (1) | DE3761471D1 (fr) |
DK (1) | DK158376C (fr) |
HK (1) | HK54691A (fr) |
NO (1) | NO168510C (fr) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE4233303C1 (de) * | 1992-10-03 | 1994-01-20 | Metallgesellschaft Ag | Verfahren zur Abtrennung von Dioxinen und Furanen aus Abgasen von Verbrennungsanlagen |
US6843835B2 (en) | 2001-03-27 | 2005-01-18 | The Procter & Gamble Company | Air cleaning apparatus and method for cleaning air |
CN1798599B (zh) * | 2003-06-03 | 2010-05-05 | 阿尔斯托姆科技有限公司 | 固体燃料燃烧的烟道气的脱汞方法和装置 |
Families Citing this family (174)
Publication number | Priority date | Publication date | Assignee | Title |
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NO125716B (fr) * | 1970-06-05 | 1972-10-23 | Norske Zinkkompani As | |
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JPS4927485A (fr) * | 1972-07-10 | 1974-03-11 | ||
AT363918B (de) * | 1975-05-06 | 1981-09-10 | Hoelter Heinz | Verfahren und vorrichtung zur gasreinigung |
JPS5338275A (en) * | 1976-09-20 | 1978-04-08 | Hitachi Ltd | Semiconductor integrated circuit and its production |
US4246242A (en) * | 1978-11-20 | 1981-01-20 | Corning Glass Works | Method of removing gaseous pollutants from flue gas |
DE3018319A1 (de) * | 1979-05-18 | 1980-11-27 | Niro Atomizer As | Verfahren zur entfernung von quecksilber aus abgasen |
JPS5631246A (en) * | 1979-08-24 | 1981-03-30 | Hitachi Ltd | Spread spectrum communication system |
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DE3426059A1 (de) * | 1984-07-14 | 1986-01-16 | Hugo Petersen Gesellschaft für verfahrenstechnischen Anlagenbau mbH & Co KG, 6200 Wiesbaden | Verfahren zur abscheidung und beseitigung von organischen schadstoffen, insbesondere von polychlorierten dibenzodioxinen (pcdd) aus rauchgasen |
DK298485A (da) * | 1985-07-01 | 1987-01-02 | Niro Atomizer As | Fremgangsmaade til fjernelse af kviksaelvdamp og dampformige chlordibenzodioxiner og -furaner fra en straem af varm raeggas |
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1986
- 1986-07-16 DK DK338186A patent/DK158376C/da not_active IP Right Cessation
-
1987
- 1987-07-07 CA CA000541419A patent/CA1300347C/fr not_active Expired - Lifetime
- 1987-07-08 US US07071191 patent/US4889698B1/en not_active Expired - Lifetime
- 1987-07-08 DE DE8787306035T patent/DE3761471D1/de not_active Expired - Lifetime
- 1987-07-08 AT AT87306035T patent/ATE49714T1/de not_active IP Right Cessation
- 1987-07-08 EP EP87306035A patent/EP0253563B2/fr not_active Expired - Lifetime
- 1987-07-14 NO NO872927A patent/NO168510C/no not_active IP Right Cessation
- 1987-07-16 JP JP62178159A patent/JPH0829219B2/ja not_active Expired - Lifetime
-
1991
- 1991-07-18 HK HK546/91A patent/HK54691A/xx not_active IP Right Cessation
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE4233303C1 (de) * | 1992-10-03 | 1994-01-20 | Metallgesellschaft Ag | Verfahren zur Abtrennung von Dioxinen und Furanen aus Abgasen von Verbrennungsanlagen |
US6843835B2 (en) | 2001-03-27 | 2005-01-18 | The Procter & Gamble Company | Air cleaning apparatus and method for cleaning air |
US7147692B2 (en) | 2001-03-27 | 2006-12-12 | The Procter & Gamble Company | Air cleaning apparatus and method for cleaning air |
CN1798599B (zh) * | 2003-06-03 | 2010-05-05 | 阿尔斯托姆科技有限公司 | 固体燃料燃烧的烟道气的脱汞方法和装置 |
Also Published As
Publication number | Publication date |
---|---|
DE3761471D1 (de) | 1990-03-01 |
NO168510C (no) | 1992-03-04 |
DK338186D0 (da) | 1986-07-16 |
JPS6323717A (ja) | 1988-02-01 |
NO872927L (no) | 1988-01-18 |
NO872927D0 (no) | 1987-07-14 |
US4889698B1 (en) | 2000-02-01 |
DK338186A (da) | 1988-01-17 |
EP0253563A1 (fr) | 1988-01-20 |
CA1300347C (fr) | 1992-05-12 |
NO168510B (no) | 1991-11-25 |
DK158376B (da) | 1990-05-14 |
ATE49714T1 (de) | 1990-02-15 |
US4889698A (en) | 1989-12-26 |
EP0253563B2 (fr) | 1996-04-17 |
HK54691A (en) | 1991-07-26 |
JPH0829219B2 (ja) | 1996-03-27 |
DK158376C (da) | 1990-10-08 |
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